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本文引用的文献

1
Denitrification, dissimilatory reduction of nitrate to ammonium, and nitrification in a bioturbated estuarine sediment as measured with N and microsensor techniques.利用 N 和微传感器技术测定生物扰动河口沉积物中的反硝化作用、硝酸盐异化还原为铵以及硝化作用。
Appl Environ Microbiol. 1992 Jan;58(1):303-13. doi: 10.1128/aem.58.1.303-313.1992.
2
Estimates of denitrification and nitrification in coastal and estuarine sediments.估算沿海和河口沉积物中的反硝化和硝化作用。
Appl Environ Microbiol. 1983 Feb;45(2):444-50. doi: 10.1128/aem.45.2.444-450.1983.
3
Method for Measuring Rates of NH(4) Turnover in Anoxic Marine Sediments, Using a N-NH(4) Dilution Technique.利用 N-NH4 稀释技术测量缺氧海洋沉积物中 NH4 转化速率的方法。
Appl Environ Microbiol. 1979 Apr;37(4):760-5. doi: 10.1128/aem.37.4.760-765.1979.
4
Capacity for denitrification and reduction of nitrate to ammonia in a coastal marine sediment.沿海海洋沉积物中反硝化和硝酸盐还原为氨的能力。
Appl Environ Microbiol. 1978 Feb;35(2):301-5. doi: 10.1128/aem.35.2.301-305.1978.
5
Effect of acetylene on nitrous oxide reduction and sulfide oxidation in batch and gradient cultures of Thiobacillus denitrificans.乙炔对脱氮硫杆菌分批培养和梯度培养中一氧化二氮还原及硫化物氧化的影响。
Appl Environ Microbiol. 1992 May;58(5):1601-8. doi: 10.1128/aem.58.5.1601-1608.1992.
6
Simultaneous determinations of nitrification and nitrate reduction in coastal sediments by a 15N dilution technique.利用¹⁵N稀释技术同时测定沿海沉积物中的硝化作用和硝酸盐还原作用。
Appl Environ Microbiol. 1978 May;35(5):853-7. doi: 10.1128/aem.35.5.853-857.1978.

采用 N 稀释技术和同位素配对法测定湖泊和河口沉积物中的硝化和反硝化作用。

Nitrification and denitrification in lake and estuarine sediments measured by the N dilution technique and isotope pairing.

机构信息

Institute of Biological Sciences, Department of Microbial Ecology, University of Aarhus, Ny Munkegade, DK-8000 Aarhus C, Denmark.

出版信息

Appl Environ Microbiol. 1993 Jul;59(7):2093-8. doi: 10.1128/aem.59.7.2093-2098.1993.

DOI:10.1128/aem.59.7.2093-2098.1993
PMID:16348987
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC182241/
Abstract

The transformation of nitrogen compounds in lake and estuarine sediments incubated in the dark was analyzed in a continuous-flowthrough system. The inflowing water contained NO(3), and by determination of the isotopic composition of the N(2), NO(3), and NH(4) pools in the outflowing water, it was possible to quantify the following reactions: total NO(3) uptake, denitrification based on NO(3) from the overlying water, nitrification, coupled nitrification-denitrification, and N mineralization. In sediment cores from both lake and estuarine environments, benthic microphytes assimilated NO(3) and NH(4) for a period of 25 to 60 h after darkening. Under steady-state conditions in the dark, denitrification of NO(3) originating from the overlying water accounted for 91 to 171 mumol m h in the lake sediments and for 131 to 182 mumol m h in the estuarine sediments, corresponding to approximately 100% of the total NO(3) uptake for both sediments. It seems that high NO(3) uptake by benthic microphytes in the initial dark period may have been misinterpreted in earlier investigations as dissimilatory reduction to ammonium. The rates of coupled nitrification-denitrification within the sediments contributed to 10% of the total denitrification at steady state in the dark, and total nitrification was only twice as high as the coupled process.

摘要

在连续流动系统中分析了在黑暗中培养的湖泊和河口沉积物中氮化合物的转化。流入的水中含有硝酸盐,通过测定流出水中 N2、硝酸盐和氨池的同位素组成,可以定量以下反应:总硝酸盐吸收、基于上层水硝酸盐的反硝化、硝化、耦合硝化-反硝化和 N 矿化。在来自湖泊和河口环境的沉积物岩心中,底栖微藻在黑暗后 25 至 60 小时内同化硝酸盐和氨。在黑暗中的稳定状态下,来自上层水的硝酸盐的反硝化占湖泊沉积物中 91 至 171 mumol m h,河口沉积物中 131 至 182 mumol m h,分别对应于两种沉积物中总硝酸盐吸收的约 100%。在早期的研究中,底栖微藻在初始黑暗期对高硝酸盐的吸收可能被误解为对铵的异化还原。在黑暗中稳定状态下,沉积物中耦合硝化-反硝化的速率占总反硝化的 10%,总硝化速率仅为耦合过程的两倍。